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Curonian Lagoon Drainage Basin Modelling and Assessment of Climate Change Impact 91 Oceanologia (2016) 58, 90—102 Available online at www.sciencedirect.com ScienceDirect jou rnal homepage: www.elsevier.com/locate/oceano ORIGINAL RESEARCH ARTICLE Curonian Lagoon drainage basin modelling and § assessment of climate change impact a b,a a c Natalja Čerkasova , Ali Ertürk , Petras Zemlys , Vitalij Denisov , d,a, Georg Umgiesser * a Open Access Centre for Marine Research, Klaipeda, Lithuania b Department of Freshwater Biology, Istanbul University, Istanbul, Turkey c Faculty of Marine Technology and Natural Sciences, Klaipeda University, Klaipeda, Lithuania d ISMAR-CNR, Institute of Marine Sciences, Venezia, Italy Received 8 September 2015; accepted 12 January 2016 Available online 9 February 2016 KEYWORDS Summary The Curonian Lagoon, which is the largest European coastal lagoon with a surface 2 2 area of 1578 km and a drainage area of 100,458 km , is facing a severe eutrophication problem. Drainage basin modelling; With its increasing water management difficulties, the need for a sophisticated hydrological SWAT; model of the Curonian Lagoon's drainage area arose, in order to assess possible changes resulting from local and global processes. In this study, we developed and calibrated a sophisticated Curonian Lagoon; hydrological model with the required accuracy, as an initial step for the future development of a Nemunas basin; modelling framework that aims to correctly predict the movement of pesticides, sediments or Climate change nutrients, and to evaluate water-management practices. The Soil and Water Assessment Tool was used to implement a model of the study area and to assess the impact of climate-change scenarios on the run-off of the Nemunas River and the Minija River, which are located in the Curonian Lagoons drainage basin. The models calibration and validation were performed using monthly 2 streamflow data, and evaluated using the coefficient of determination (R ) and the Nash-Sutcliffe 2 model efficiency coefficient (NSE). The calculated values of the R and NSE for the Nemunas and Minija Rivers stations were 0.81 and 0.79 for the calibration, and 0.679 and 0.602 for the validation period. Tw o potential climate-change scenarios were developed within the general § This study was funded by the European Social Fund under the Global Grant measure (CISOCUR project VP1-3.1-ŠMM-07-K-02-086). * Corresponding author at: ISMAR-CNR, Institute of Marine Sciences, Arsenale — Tesa 104, Castello 2737/F, 30122 Venezia, Italy. Tel.: +39 339 4238653. E-mail address: [email protected] (G. Umgiesser). Peer review under the responsibility of Institute of Oceanology of the Polish Academy of Sciences. http://dx.doi.org/10.1016/j.oceano.2016.01.003 0078-3234/# 2016 Institute of Oceanology of the Polish Academy of Sciences. Production and hosting by Elsevier Sp. z o.o. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Curonian Lagoon drainage basin modelling and assessment of climate change impact 91 patterns of near-term climate projections, as defined by the Intergovernmental Panel on Climate Change Fifth Assessment Report: both pessimistic (substantial changes in precipitation and temper- ature) and optimistic (insubstantial changes in precipitation and temperature). Both simulations produce similar general patterns in river-discharge change: a strong increase (up to 22%) in the winter months, especially in February, a decrease during the spring (up to 10%) and summer (up to 18%), and a slight increase during the autumn (up to 10%). # 2016 Institute of Oceanology of the Polish Academy of Sciences. Production and hosting by Elsevier Sp. z o.o. This is an open access article under the CC BY-NC-ND license (http://creativecommons. org/licenses/by-nc-nd/4.0/). 2010). As a result, the lagoon's water level is usually higher 1. Introduction than that of the Baltic Sea; therefore, the dominant currents 0 are from the lagoon to the Baltic Sea. The Curonian Lagoon is located at N 55830 latitude and 0 Over the years, the water discharge to the lagoon chan- E 21815 longitude. It is the largest European coastal lagoon, ged, and this led to a fluctuation of the water balance. Major separated from the Baltic Sea by a narrow 0.5—4 km wide changes have been observed in the last decade in the winter— sandy Curonian spit and connected to the Baltic Sea through spring period. In the winter months of January and February, the Klaipeda Strait. Several small rivers — such as the Bol- due to observed warmer winters, the Nemunas' run-off has shaya and Malaya Morianka, Kalinovka, Deima, Rybnaya, increased, while spring floods are decreasing; therefore, run- Minija, Dane and Dreverna — and one large river (Nemunas) off levels over the year became more homogeneous (Žilinskas discharge into the Curonian Lagoon. The southern and central et al., 2012). parts of the lagoon contain fresh water due to the discharge Agriculture has a significant impact on the status of water from those rivers. The run-off of rivers to the lagoon varies 3 3 À1 3 À1 bodies in the Nemunas River basin, especially in the sub-basins from 14 to 33 km per year (444 m s to 1046 m s ) and of the Sesupe and Nevezis Rivers; this factor has a local, but exhibits a strong seasonal pattern, peaking with snowmelt serious, impact. Chemicals that enter the river from agricul- during the flood season of March to April (Dubra and ture and fishponds are a major source of pollution. A substan- Červinskas, 1968). tial proportion of point-source pollution comes from industry. The area of land draining into the Curonian Lagoon covers 2 According to the Second Assessment of Transboundary Rivers, 100,458 km , of which 48% lies in Belarus, 46% in Lithuania, Lakes and Groundwaters by the United Nations Economic and 6% in the Kaliningrad Oblast and Poland (Gailiušis et al., Commission for Europe (2011), there is room for development 1992) (see Fig. 1). The drainage area of the Curonian Lagoon in the monitoring of the Nemunas River, as the current list of consists of several river basins; however, the most important monitored pollutants is limited. There is a lack of biological of them is the Nemunas River drainage basin in terms of flow observation and monitoring of pollutants in river-bottom sedi- rates and nutrient inputs, supplying about 98% of its inflows ments, and a joint, harmonized monitoring programme for the (Jakimavičius, 2012). The annual Nemunas River water transboundary watercourses is needed. It is important to inflow into the Curonian Lagoon is more than three times develop a model for nutrient and other biogeochemically greater than the volume of water in the lagoon (Žilinskas significant dissolved-substance contributions that are altering et al., 2012). According to researchers, the average annual 3 3 À1 and influencing the ecosystems of the Nemunas River and run-off during 1812 to 2002 was 22.054 km (699 m s ) Curonian Lagoon. (Gailiušis et al., 1992), and from 1960 to 2007 it was 3 3 À1 The first step is the development of a hydrological model 21.847 km (692 m s ) (Jakimavičius and Kovalenkovienė, and analysis of changes in the Curonian Lagoon drainage basin due to global processes (climate change, etc.), as well as local anthropogenic activities, and forecasting possible changes in the future. Model hydrology calibration, uncer- tainty analysis and sensitivity analysis enables a broader understanding of key processes in the catchment area. Recent work conducted in the field of Curonian Lagoon drainage basin modelling is reported in the doctoral disserta- tion “Changes of water balance elements of the Curonian Lagoon and their forecast due to anthropogenic and natural factors” by Jakimavičius (2012). In this work, the author had created hydrological models for the separate Nemunas catch- ment areas using HBV (Hydrologiska Byråns Vattenbalansav- delning), before calibrating and validating them. The sensitivity and uncertainty of the Nemunas run-off model parameters were assessed using the SUSA (Software for Uncertainty and Sensitivity Analyses) package. Hydrometeor- ological information of the period 1961—1990 was used for the model's creation. The period 1961—1975 was selected for the model's calibration, whereas the period 1976—1990 Figure 1 Curonian Lagoon drainage area. 92 N. Čerkasova et al. was used for its validation. Prognostic data from 14 measure- model that operates on a daily time step and is designed ment stations, data from 1961 to 1990 and the downscaling to predict the impact of management on water, sediment, method were applied to calculate the daily mean data from and agricultural chemical yields in ungauged drainage areas the mean monthly output data of climate-change scenarios. (Arnold et al., 1993). In this way, obtained prognostic values of precipitation and The drainage basin area was divided into multiple sub- temperature data were used to simulate the Nemunas' inflow basins, which were then further subdivided into Hydrological and to compute its water balance (Jakimavičius, 2012). Response Units that consist of homogeneous land-use, man- Projections of the temperature and precipitation of the agement and soil characteristics (Arnold et al., 1993). Using Nemunas' river basin for the 21st century (according to the SWAT, run-off was predicted for each HRU separately and conclusions of the Fourth Assessment Report of the United routed to obtain the total run-off of a catchment area. This Nations Intergovernmental Panel on Climate Change, as well solution improves the model's accuracy and provides a much as the results of output data of ECHAM5 and HadCM3 global better physical description of the water balance (Neitsch climate models under A2, A1B and B1 greenhouse gas emis- et al., 2011). sion scenarios) were used to create the climate-change A stable version of the SWAT from 2009 was used due to the scenarios.
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